Nanoparticle Aerosol Generator

Abstract

A nanoparticle aerosol generator, comprised of a vibrating fluidized bed with a baffle, a vibrating Venturi disperser and a cyclone separator. To generate nanoparticle aerosols, the nanoparticle aerosol generator uses the multiple impaction, vibrating air flow and vibrating high speed air flow to break up larger agglomerates, and multiple dilution to minimize the re-agglomeration of the particles.

Description

CROSS-REFERENCE TO RELATED APPLICATIONS

This application claims priority to U.S. provisional application No. 61/455,355 filed on Oct. 19, 2011.

REFERENCE TO SEQUENCE LISTING, A TABLE, OR A COMPUTER PROGRAM LISTING COMPACT DISC APPENDIX

Not Applicable

BRIEF DESCRIPTION OF THE SEVERAL VIEWS OF THE DRAWINGS

FIG. 1 is a perspective view of the nanoparticle aerosol generator.

FIG. 2 is SMPS measurements of TiO₂ aerosol generated by the embodied nanoparticle aerosol generator particle size distribution where N=the number of particles, D=geometric diameter.

FIG. 3 is SMPS measurements of TiO2 aerosol generated by the embodied nanoparticle aerosol generator mass concentration vs. time where N=the number of particles, D=geometric diameter.

FIG. 4 is SMPS measurements of TiO2 aerosol generated by the embodied nanoparticle aerosol generator particle size vs. time where N=the number of particles, D=geometric diameter.

FIG. 5 is ELPI measurements of TiO₂ aerosol generated by the embodied nanoparticle aerosol generator particle size where N=the number of particles, Dp=aerodynamic diameter.

FIG. 6 is ELPI measurements of TiO2 aerosol generated by the embodied nanoparticle aerosol generator mass concentration vs. time where N=the number of particles, Dp=aerodynamic diameter.

FIG. 7 is ELPI measurements of TiO2 aerosol generated by the embodied nanoparticle aerosol generator particle size vs. time where N=the number of particles, Dp=aerodynamic diameter.

FIG. 8 is a graph of the relative concentration of TiO₂ aerosol generated by a TSE Bundschuh dust generator, measured with TSE dust concentration monitor.

FIG. 9 is a graph of the relative concentration of TiO₂ aerosol generated by a TSE Wright dust generator measured with TSE dust concentration monitor.

FIG. 10 is ELPI measurements of CeO₂ aerosol generated by the embodied nanoparticle aerosol generator particle size distribution where N=the number of particles, Dp=aerodynamic diameter.

FIG. 11 is ELPI measurements of CeO2 aerosol generated by the embodied nanoparticle aerosol generator mass concentration vs. time where N=the number of particles, Dp=aerodynamic diameter.

FIG. 12 is ELPI measurements of CeO2 aerosol generated by the embodied nanoparticle aerosol generator particle size vs. time where N=the number of particles, Dp=aerodynamic diameter.

DETAILED DESCRIPTION OF THE INVENTION

The study of the health effects of nano-sized aerosol particles requires the particles delivered to the laboratory animals in the exposure chamber to have: (1) a consistent concentration maintained at a desired level for hours, (2) a homogenous composition free from contaminants, and (3) a size distribution with a geometric mean diameter<200 nm and a geometric standard deviation σ_g<2.5 (Schmoll et al, 2009). Generation of nanoparticle aerosols at concentrations sufficient to perform toxicology studies is highly challenging because nanoparticles tend to agglomerate due to very strong inter-particle forces and form large fractal structures in tens or hundreds of microns in size (To et al, 2009), which are difficult to be broken up, especially for sticky or cohesive powders such as nano-TiO₂ dry powder.

In order to perform inhalation studies, the test aerosols can be created by aerosolizing a particle bulk powder. Some common aerosol generators used for this purpose include nebulizers, fluidized beds, Venturi aspirators, and the Wright dust feed (Willeke 1980). However, past test aerosol production typically focused on producing aerosols with a size distribution with median diameter greater than 1 μm (Schmoll et al, 2009). Recently, five different generation methods for producing a nanoparticle aerosol from the bulk powder were evaluated with the goal of producing an acceptable nanoparticle aerosol, however, none of the devices were able to satisfy all criteria for an acceptable aerosol (Schmoll et al, 2009). Existing aerosol generators can not create aerosols in the size range, concentration and duration which are necessary for nanoparticle inhalation toxicology studies. This is particularly true for inhalation exposure chambers such as with a volume of 0.5 m³ or more.

The embodied nanoparticle aerosol generator, consisting of a vibrating fluidized bed with a baffle and a vibrating Venturi disperser as well as a cyclone separator, utilizes vibrating high speed shear flow and multiple impaction to disperse larger agglomerates of nanoparticles. Additionally it can use multiple dilution to minimize re-agglomeration of the particles. The particle size and mass concentration produced by the nanoparticle aerosol generator can be controlled by adjusting flow rate of air through dry powder layer, and vibration frequency and amplitude.

A first embodiment, as shown in FIG. 1, is a nanoparticle aerosol generator consists of a vibrating fluidized bed with a baffle, a vibrating Venturi disperser and a cyclone separator. The vibrating fluidized bed with a baffle is comprised of a cylinder 101 with a proximal and distal ends that can have at least two air feed ports, one port on the proximal end 102 and the other on the distal end 103, and an exit port 104 on the cylinder top which can be connected to a vibrating Venturi disperser 105 which can be connected to a cyclone separator 106. A vibrator 107 attached to the cylinder can produce mechanical vibrations. Sample/nanoparticle dry powder 108 to be aerosolized can rest on a filter 109 supported by a stainless steel air distributor 110 on the proximal end in the cylinder. A stainless steel screen 111 can be placed in the sample/dry powder to break up larger agglomerates. A further embodiment of the nanoparticle aerosol generator can include a baffle 112 which is connected around the exit port. The vibrating cylinder further can be used as a vibrating fluidized bed with a baffle.

Another embodiment of the nanoparticle aerosol generator can include a cylinder 101 made of metal or other materials. A vibrator is attached to the cylinder. The cylinder can have a proximal and a distal end. Both ends can have air feed ports 102, 103. These air feed ports can have their control valves and flow meters 113, 114, and air feed tubes 115 attached in which clean and dry air can be pulled into the cylinder through an activated carbon and HEPA filter 116. The cylinder can also have an exit port 104 on the top. A stainless steel air distributor 110 can be placed above the air feed port 102 on the proximal end in the cylinder. A filter 109 can sit on the stainless steel air distributor 110. Sample/nanoparticle dry powder 108 to be aerosolized can be rest on the filter 109. A stainless steel screen 111 with a diameter just smaller than the inner diameter of the cylinder can be placed in the sample/nanoparticle dry powder. The stainless steel screen 111 can break up larger agglomerates through the impaction between sample and the stainless steel screen. Without the stainless steel screen the output aerosol concentration can be much lower. The vibrating cylinder can induce pressure wave/fluctuation in the air which carries the particles, especially in the air nearby the inner surface of the cylinder. The air pressure wave/fluctuation can help break up the larger agglomerates. Mechanical vibrations can be produced by a vibrator attached to the proximal end of the cylinder. The vibration can be agitated by any known agitation mechanism known to one skilled in the art. Mechanical vibration can be applied parallel with the axis of the cylinder.

The baffle 112 can be a stainless steel tubing or other material tubing with one dead-end and one open-end. The open-end can be of an effective diameter to be attached in the center of the vibrating cylinder around its exit port 104. A hole 117 near the open-end of the baffle can be used as the aerosol exit in the baffle. The dead-end of the tubing 112 can extend to just above the top of the sample/dry powder 108. The baffle vibrating with the cylinder can transfer the mechanical vibrating energy to the center region of the air that carries the particles in the cylinder. The air flow pressure wave/fluctuations induced by the vibration can help destroy cohesions between particles. When the aerosol flows upward, some of the larger agglomerates can be removed from aerosol streams by the baffle 112. Without the baffle, the size of the output particles is much larger.

The mechanical vibration not only generates pressure wave/fluctuations in the air flow to destroy cohesions between particles, but also reduces deposition of the particles on the inner surface of the cylinder and the outer surface of baffle. In the embodied nanoparticle aerosol generator, the extra mechanical vibration energy is transferred to the air flow that carries the particles, and eventually, the energy is used to help destroy cohesions between particles efficiently.

The Venturi disperser 105 can be connected to the exit port 104 of the vibrating cylinder. The Venturi disperser vibrates with the vibrating cylinder. The Venturi disperser has a constriction 118 in a pipe. A high-velocity air jet blowing across the constriction 118 in the Venturi disperser, can create a vacuum in the cylinder 101 and clean and dry air can be drawn into the cylinder from the air feed ports on the both proximal and distal ends through an activated carbon and HEPA filter 116. A portion of the air drawn in from the proximal end air feed port 102 will flow through the dry powder layer 108 in the cylinder to carry some small particles upward to form an aerosol stream, and will move towards the exit port 104, while the rest of air enters the cylinder through the air feed port 103 on distal end and mixes with the upward flowing aerosol stream. The air flow from the distal end air feed port will hit the crossflow aerosol stream resulting in some larger particles being removed from the aerosol stream. The aerosol can also be diluted by the clean and dry air, which helps reduce the probability of re-agglomeration of the particles. When the aerosol stream flows nearby the hole 117 in the baffle 112, some larger particles will be removed because they not able to follow the air to make a 90° turn to enter the hole 117. Smaller particles can follow the air flow to leave the cylinder. Once the aerosol enters the Venturi disperser, particles will impact on a tube 119 in the Venturi disperser first. The large particles will be dispersed by this impaction, while smaller particles will follow the air flow to mix with vibrating high speed shear flow in the Venturi disperser. The vibrating high speed shear flow will continuously disperse the agglomerates, dilute the aerosol, and deliver the aerosol to the cyclone separator 106. In the cyclone separator the larger particle can be separated. After passing the cyclone separator 106, the aerosol mixes with clean and dry air in a mixing device (which is not shown in FIG. 1) to achieve desired concentrations. The aerosol can be diluted in the mixing device. The dilution can reduce the probability of the particle re-agglomeration before the aerosol enters the inhalation exposure chamber. The use of the Venturi disperser allows for the pressure in the cylinder to be slightly negative. Negative pressure in the cylinder can prevent the particles or other toxin material from escaping from the cylinder. Unlike most of the conventional Venturi dispersers use high speed shear flow to break up large agglomerates, this embodiment uses a vibrating high speed shear flow and multiple impaction to disperse larger agglomerates. The particle size and mass concentration can be controlled via adjusting: (1) flowrate of air passing through the dry powder layer with valve 113; and (2) the vibration frequency and amplitude. The higher air flowrate through the dry powder layer, the higher aerosol concentration. For example, the nano-sized TiO₂ aerosol mass concentration can be increased to 12 mg/m³ from 6.2 mg/m³ in the inhalation exposure chamber when the air flowrate through the dry powder is increased to 3 LPM from 1.5 LPM.

Characterization of aerosols generated by nanoparticle aerosol generator. In order to test the dust/aerosol generators, nano-sized TiO₂ dry powder (Aeroxide P25, Evonik, Germany) with primary diameter of 21 nm and density of 3.7 g/cm³ and nano-sized CeO₂ dry powder with primary diameter of 3 nm and density of 7.1 g/cm³ were used. Three dust/aerosol generators were tested for the ability to generate nanoparticle aerosols having: (1) a consistent concentration maintained at a desired level for hours, (2) a homogenous composition free contaminants, and (3) a size distribution with a geometric mean diameter<200 nm and geometric standard deviation σ_g<2.5. Before being aerosolized, TiO₂ or CeO₂ dry powders were conditioned in a dry desiccator for 24 hours. The aerosols were delivered to a 0.5 m³ stainless steel inhalation exposure chamber for the measurements.

Measurement Methods:

An electric low pressure impactor (ELPI) (Dekati Inc., Finland), a scanning mobility particle sizer (SMPS) (TSI Inc., Shoreview, Minn., USA) were used to measure real time particle size distributions and relative mass concentration of the particles in the inhalation exposure chamber. A TSE dust concentration monitor (TSE Systems GmbH, German) was used to monitor relative concentration of the aerosols generated by TSE dust generators (TSE Systems GmbH, German). The real mass concentrations of the aerosols were determined gravimetrically.

Experimental Results:

TiO₂ Aerosols:

Two embodied nanoparticle aerosol generators were operated simultaneously to deliver TiO₂ aerosols to a 0.5 m³ inhalation exposure chamber at flowrate of 90 LPM. The air flow rate through the dry powder layer in each nanoparticle aerosol generator was 1.5 LPM. A pneumatic vibrator driven by 60 psi compressed air was used to produce mechanical vibration. FIGS. 2A-2C are the particle size distribution, particle mass concentration and particle mean geometric diameter evolution measured with the SMPS. As can be seen from FIGS. 2A-2C, when the particle concentration reaches the desired concentration in the inhalation exposure chamber, the aerosol generated by the nanoparticle aerosol generators has: (1) a geometric mean diameter=157 nm with a standard deviation σ_g=2.3 (FIG. 2); (2) a relatively stable particle mass concentration of 6.2 mg/m³ during a 5-hour-study (FIG. 3); (3) a stable particle size with a relative deviation less than 7% during 5-hour-study (FIG. 4). FIGS. 5-7 are the aerodynamic diameter distribution, relative mass concentration, and particle size evolution measured with the ELPI. The count-median aerodynamic diameter of the particles is 152 nm. The relative mass concentration of the particles is stable during a 5-hour-study. FIGS. 8 and 9 are the particle concentrations of TiO₂ aerosols generated by TSE Bundschuh dust generator and TSE Wright dust generator. The particle concentration of the aerosols generated by TSE dust generators could not be maintained at a constant level. The outcome of the studies is summarized in Table 1.

TABLE 1
		Test
	Dust Generator	location	Outcome
1	TSE Bundschuh	Our lab	A nozzle Venturi disperser was blocked
	dust generator		by the nano TiO2 particles after several
			minutes.
2	TSE Wright	Our lab	No stable generation and output hole of
	dust generator		the particles was blocked nano by TiO2
			particles after 30-40 minutes.
3	Nanoparticle	Our lab	Nanoparticle aerosol concentration
	aerosol generator		remained stable for hours

CO₂ Aerosols:

One embodied nanoparticle aerosol generator was operated to generate CeO₂ aerosols from nano-sized CeO₂ dry powder. The air flow rate through the CeO₂ dry powder layer in the nanoparticle aerosol generator was 1.5 LPM. The aerosol was delivered to a 0.5 m³ inhalation exposure chamber at flowrate of 90 LPM and measured with the ELPI. FIGS. 10-12 are the particle size distribution, particle relative mass concentration and particle count median aerodynamic diameter evolution measured with the ELPI. As can be seen from FIGS. 10-12, when the particle concentration reaches the desired concentration in the inhalation exposure chamber, the CeO₂ aerosol generated by the nanoparticle aerosol generators has: (1) a count median aerodynamic diameter=145.4 nm (FIG. 10); (2) a relatively stable particle mass concentration during a 3-hour-study (FIG. 11); (3) a relative stable particle size during a 3-hour-study (FIG. 12).

Among the tested aerosol/dust generators, the embodied nano-particle aerosol generator is the only one that can generate nanoparticle aerosols from nano-TiO₂ or CeO₂ dry powder directly.

These terms and specifications, including the examples, serve to describe the invention by example and not to limit the invention. It is expected that others will perceive differences, which, while differing from the forgoing, do not depart from the scope of the invention herein described and claimed. In particular, any of the function elements described herein may be replaced by any other known element having an equivalent function.

REFERENCES

• 1. Schmoll L H, Elzey S., Grassian V H, O'shaughnessy P T., 2009, Nanoparticle aerosol generation methods from bulk powders for inhalation exposure studies. Nanotoxicology, 3(4): 265-275
• 2. To D, Dave R, Yin X, Sundaresan S, 2009, Deagglomeration of Nanoparticle Aggregates via Rapid Expansion of Supercritical or High-Pressure Suspensions, AIChE Journal, Vol. 55, No. 11, 2087-2026
• 3. Willeke K, editor. 1980. Generation of aerosols and facilities for exposure experiments. Ann Arbor Science Publishers.

Claims

1. A device comprising a nanoparticle aerosol generator capable of multiple dilution to minimize the re-agglomeration of the particles wherein the nanoparticle aerosol is comprised of a vibrating fluidized bed with a baffle wherein the vibrating fluidized bed with a baffle is further comprised of a cylinder wherein the cylinder has; wherein the vibrating Venturi disperser can create a negative pressure in the vibrating cylinder.

a proximal and distal end each end containing one or more air feed ports wherein the air feed ports connect to air feed tubes in which clean air can be pulled into the cylinder;

an exit port at the distal end above the distal air feed port wherein the exit port is connected to a vibrating Venturi dispenser the vibrating Venturi dispenser further connected to a cyclone separator;

a vibrator attached outside the proximal end;

a filter for a sample to be placed wherein the filter is supported by a stainless steel air distributor attached in the proximal end above the proximal air feed port;

a baffle attached at the distal end of the cylinder around the exit port wherein the baffle has a hole near the attachment point for an exit port;

2. The device of claim 1 wherein a stainless steel screen is placed in the sample.

3. The device of claim 1 wherein the air feed lines are further comprised of control valves and flow meters.

4. The device of claim 3 wherein the control valves can control the particle size and mass concentration of a sample by adjusting airflow rates through the sample.

5. The device of claim 1 wherein the air feed tubes attach to a filter.

6. The device of claim 5 wherein the filter is an activated carbon and HEPA filter.

7. The device of claim 1 wherein the baffle extends into the proximal end to an area just above the top of the area for the sample.

8. The device of claim 1 wherein the cyclone separator is attached to a mixing device to mix the aerosol with air to a desired concentration.

9. The device of claim 1 wherein the particle size and mass concentration of a sample can be controlled by adjusting the vibration frequency and amplitude of the vibrator.